CN105016555A - Garbage fly ash water washing liquid evaporation desalination system and method - Google Patents
Garbage fly ash water washing liquid evaporation desalination system and method Download PDFInfo
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Abstract
本发明公开了一种垃圾飞灰水洗液蒸发脱盐系统和方法,所述系统将蒸发浓缩和蒸发结晶分为两个相对独立的单元,所需热能由压缩机系统提供和维持平衡;蒸发浓缩单元包括预热器、降膜蒸发器和降膜分离器,通过对垃圾飞灰水洗液预热、反复蒸发,物料得到了浓缩;蒸发结晶单元包括强制循环分离器、强制循环蒸发器,浓缩物料经过进一步蒸发后,物料达到了饱和或过饱和状态,结晶盐开始析出;本发明后续设置稠厚器和离心机,通过稠厚器沉降浓缩和离心机分离后,垃圾飞灰水洗液中的盐得以最终分离。上述系统适应了垃圾飞灰水洗液成分复杂且含盐浓度高的特点,具有蒸发能力大,运行稳定和脱盐顺畅的特点,从而保证了垃圾飞灰水洗液得到规模化稳定处置。
The invention discloses a system and method for evaporative desalination of garbage fly ash water washing liquid. The system divides evaporative concentration and evaporative crystallization into two relatively independent units, and the required heat energy is provided and maintained by a compressor system; the evaporative concentration unit Including preheater, falling film evaporator and falling film separator, through preheating and repeated evaporation of garbage fly ash washing liquid, the material is concentrated; evaporation and crystallization unit includes forced circulation separator, forced circulation evaporator, concentrated material passes through After further evaporating, the material reaches a saturated or supersaturated state, and crystallized salt begins to precipitate; the present invention subsequently sets up a thickener and a centrifuge, and after the thickener settles and concentrates and the centrifuge separates, the salt in the garbage fly ash washing liquid can be recovered. eventually separated. The above-mentioned system adapts to the characteristics of complex components of garbage fly ash washing liquid and high salt concentration, and has the characteristics of large evaporation capacity, stable operation and smooth desalination, thus ensuring large-scale and stable disposal of garbage fly ash washing liquid.
Description
技术领域technical field
本发明涉及蒸发脱盐技术领域,对成分复杂且浓度高的含盐水蒸发脱盐尤其适用,具体地讲,涉及一种垃圾飞灰水洗液蒸发脱盐系统和方法。The invention relates to the technical field of evaporative desalination, and is especially suitable for evaporative desalination of salty water with complex components and high concentration. Specifically, it relates to an evaporative desalination system and method for garbage fly ash washing liquid.
技术背景technical background
垃圾飞灰是指在垃圾焚烧发电厂烟气净化系统收集而得的残余物,含有二恶英、呋喃等有机污染物和Pb、Cr等可溶性重金属,对环境和人体健康危害大,必须进行安全有效处置。根据垃圾飞灰成分特性,作为原料烧结水泥是一种有效处置垃圾飞灰的方法,但是垃圾飞灰中氯离子含量高,直接作为水泥原料会产生结皮和堵塞,影响水泥窑的正常运行,因此需要对垃圾飞灰进行预处理。Garbage fly ash refers to the residue collected from the flue gas purification system of waste incineration power plants. It contains organic pollutants such as dioxins and furans and soluble heavy metals such as Pb and Cr. Effective disposal. According to the composition characteristics of waste fly ash, sintering cement as raw material is an effective method to dispose of waste fly ash, but the content of chloride ion in waste fly ash is high, and directly used as cement raw material will cause skinning and blockage, which will affect the normal operation of cement kiln. Therefore, it is necessary to pretreat the fly ash of garbage.
诸多研究和试验表明,水洗是一种有效的预处理方法,垃圾飞灰经过水洗预处理后,氯离子含量大幅度降低,满足并适合后续水泥窑处置,但是水洗产生的垃圾飞灰水洗液因含有较高浓度的氯盐需要进行蒸发脱盐处置。专利号为ZL201110031075.2的中国发明专利“一种从垃圾焚烧飞灰中提取钾钠盐的系统和方法”公开了一种从垃圾飞灰水洗液中提取钾钠盐单元,其主要包括预热器、蒸发器、闪蒸结晶器和蒸汽机械压缩器等,该单元实际上是一种非常简单的MVR(机械式蒸汽再压缩)系统,虽然相比传统蒸发方式具有节能效果明显的特点,但是由于垃圾飞灰水洗液中含有的盐包括氯化钠、氯化钾、碳酸钠、氯化钙等,成分复杂,且含盐浓度高,使得上述单元在实际运行中出现蒸发能力低、稳定性差和出盐不畅等问题,因此需要对该单元进行创新式改进。Many studies and experiments have shown that water washing is an effective pretreatment method. After the waste fly ash is pretreated by water washing, the chloride ion content is greatly reduced, which is suitable for subsequent cement kiln disposal. Containing a higher concentration of chlorine salt requires evaporative desalination. The Chinese invention patent with the patent number ZL201110031075.2 "A system and method for extracting potassium and sodium salts from garbage incineration fly ash" discloses a unit for extracting potassium and sodium salts from garbage fly ash washing liquid, which mainly includes preheating device, evaporator, flash crystallizer and steam mechanical compressor, etc. This unit is actually a very simple MVR (Mechanical Vapor Recompression) system. Since the salt contained in the waste fly ash washing liquid includes sodium chloride, potassium chloride, sodium carbonate, calcium chloride, etc., the composition is complex and the salt concentration is high, which makes the above units have low evaporation capacity and poor stability in actual operation. And problems such as poor salt discharge, so it is necessary to make innovative improvements to this unit.
发明内容Contents of the invention
为了解决现有技术中存在的问题,本发明的目的是提供一种垃圾飞灰水洗液蒸发脱盐系统,以及利用该系统对垃圾飞灰水洗液进行蒸发脱盐的方法,从而适应了垃圾飞灰水洗液成分复杂且含盐浓度高的特点,保证垃圾飞灰水洗液得到规模化稳定处置。In order to solve the problems existing in the prior art, the object of the present invention is to provide a garbage fly ash water washing liquid evaporation desalination system, and a method for evaporative desalination of the garbage fly ash water washing liquid using the system, thereby adapting to the garbage fly ash water washing The characteristics of complex liquid composition and high salt concentration ensure large-scale and stable disposal of garbage fly ash washing liquid.
为了实现上述目的,本发明采用如下的技术方案:In order to achieve the above object, the present invention adopts the following technical solutions:
一种垃圾飞灰水洗液蒸发脱盐系统,包括预热器、降膜蒸发器、降膜分离器、强制循环分离器、强制循环蒸发器、稠厚器、离心机、母液罐、压缩机系统和冷凝水罐,其中,预热器冷媒进口前安装有进料泵,预热器冷媒出口与降膜蒸发器进料口相连;降膜蒸发器出料口与降膜分离器进口连接;降膜分离器设有两个液体出口,其一液体出口通过循环泵与降膜蒸发器进料口连接,另一液体出口通过转料泵与强制循环分离器一液体进口连接;强制循环分离器设置有三个液体进口和两个液体出口,其中一个液体进口与强制循环蒸发器出料口相连,其中一个液体出口通过强制循环泵与强制循环蒸发器进料口相连,另一个液体出口通过出料泵与稠厚器进口相连,第二个液体进口通过母液泵与母液罐出口连接;稠厚器溢流口与母液罐一进口连接,稠厚器下料口与离心机进料口连接;离心机母液出口与母液罐另一进口连接;降膜分离器与强制循环分离器蒸汽出口经管道汇合后与压缩机系统蒸汽进口相连;压缩机系统蒸汽出口与强制循环蒸发器蒸汽进口连接;强制循环蒸发器蒸汽出口与降膜蒸发器蒸汽进口连接,强制循环蒸发器冷凝水出口与和冷凝水罐一进口连接,降膜蒸发器冷凝水出口与冷凝水罐另一进口连接;冷凝水罐出口通过冷凝水泵与预热器热媒进口连接。An evaporative desalination system for garbage fly ash washing liquid, including a preheater, a falling film evaporator, a falling film separator, a forced circulation separator, a forced circulation evaporator, a thickener, a centrifuge, a mother liquor tank, a compressor system and Condensate water tank, in which, a feed pump is installed before the refrigerant inlet of the preheater, and the refrigerant outlet of the preheater is connected with the inlet of the falling film evaporator; the outlet of the falling film evaporator is connected with the inlet of the falling film separator; The separator is equipped with two liquid outlets, one of which is connected to the feed port of the falling film evaporator through a circulation pump, and the other liquid outlet is connected to the liquid inlet of the forced circulation separator through a material transfer pump; the forced circulation separator is equipped with three One liquid inlet and two liquid outlets, one of which is connected to the outlet of the forced circulation evaporator, one of the liquid outlets is connected to the inlet of the forced circulation evaporator through a forced circulation pump, and the other liquid outlet is connected to the outlet of the forced circulation evaporator through a discharge pump The thickener inlet is connected, and the second liquid inlet is connected with the outlet of the mother liquor tank through the mother liquor pump; the overflow port of the thickener is connected with the first inlet of the mother liquor tank, and the feeding port of the thickener is connected with the feed port of the centrifuge; the centrifuge mother liquor The outlet is connected to the other inlet of the mother liquor tank; the steam outlet of the falling film separator and the forced circulation separator are connected to the steam inlet of the compressor system after being joined by a pipeline; the steam outlet of the compressor system is connected to the steam inlet of the forced circulation evaporator; the forced circulation evaporator The steam outlet is connected to the steam inlet of the falling film evaporator, the condensed water outlet of the forced circulation evaporator is connected to the first inlet of the condensed water tank, and the condensed water outlet of the falling film evaporator is connected to the other inlet of the condensed water tank; the outlet of the condensed water tank is connected to the condensed water pump Connect with the heat medium inlet of the preheater.
所述预热器为板式换热器。The preheater is a plate heat exchanger.
所述降膜蒸发器上部设有布液盘。The upper part of the falling film evaporator is provided with a liquid distribution pan.
所述离心机为两级活塞推料离心机或卧螺离心机。The centrifuge is a two-stage piston pusher centrifuge or a decanter centrifuge.
所述强制循环分离器为正循环切向进料蒸发器。The forced circulation separator is a positive circulation tangential feed evaporator.
为了实现上述目的,本发明采用的另一个技术方案为:In order to achieve the above object, another technical solution adopted by the present invention is:
一种垃圾飞灰水洗液蒸发脱盐方法,包括如下步骤:A method for evaporating and desalting garbage fly ash water washing liquid, comprising the steps of:
1)将预处理后的垃圾飞灰水洗液用泵打入预热器进行加热,加热热媒为换热后的冷凝水;1) Pump the pretreated garbage fly ash water washing solution into the preheater for heating, and the heating medium is condensed water after heat exchange;
2)预热后物料进入降膜蒸发器进行蒸发浓缩,控制降膜蒸发器内的蒸发温度为103-107℃;2) After preheating, the material enters the falling film evaporator for evaporation and concentration, and the evaporation temperature in the falling film evaporator is controlled to be 103-107°C;
3)蒸发浓缩接近饱和状态的物料进入降膜分离器进行气液分离,分离后蒸汽进入压缩机系统,分离后一部分液体通过泵返回降膜蒸发器继续蒸发,另一部分液体由泵打入强制循环分离器;3) Evaporated and concentrated materials that are close to saturation enter the falling film separator for gas-liquid separation. After separation, the steam enters the compressor system. After separation, part of the liquid returns to the falling film evaporator through the pump to continue evaporation, and the other part of the liquid is injected into the forced circulation by the pump. Splitter;
4)强制循环分离器内物料通过外接的强制循环蒸发器进行深度蒸发浓缩,控制强制循环分离器内液相温度为108-112℃;4) The material in the forced circulation separator is subjected to deep evaporation and concentration through an external forced circulation evaporator, and the temperature of the liquid phase in the forced circulation separator is controlled to be 108-112°C;
5)强制循环分离器内物料达到饱和或过饱和后迅速气液分离,分离后蒸汽进入压缩机系统,分离后液体有小颗粒结晶盐析出,结晶盐下落至强制循环分离器底部后由泵送入稠厚器;5) After the material in the forced circulation separator reaches saturation or supersaturation, the gas-liquid separation is rapid. After separation, the steam enters the compressor system. After separation, the liquid has small particles of crystalline salt precipitated, and the crystalline salt falls to the bottom of the forced circulation separator and is pumped. into the thickener;
6)含有结晶盐物料在稠厚器内沉降后,上清液溢流至母液罐,浓缩物料进入离心机分离后得到结晶盐,而离心母液进入母液罐,母液罐物料由泵打入强制循环分离器内继续蒸发浓缩;6) After the material containing crystalline salt settles in the thickener, the supernatant overflows to the mother liquor tank, and the concentrated material enters the centrifuge for separation to obtain crystalline salt, while the centrifuged mother liquor enters the mother liquor tank, and the mother liquor tank material is pumped into forced circulation Continue to evaporate and concentrate in the separator;
7)进入压缩机系统的蒸汽经过加压升温至116-118℃后,进入强制循环蒸发器和降膜蒸发器加热物料,经过换热的冷凝水进入冷凝水罐后由泵送至预热器对垃圾飞灰水洗液进行加热。7) After the steam entering the compressor system is pressurized and heated to 116-118°C, it enters the forced circulation evaporator and falling film evaporator to heat the material, and the condensed water after heat exchange enters the condensed water tank and is pumped to the preheater The garbage fly ash washing solution is heated.
进一步的,垃圾飞灰水洗液经过预热器加热后进行第二次加热。Further, the garbage fly ash washing liquid is heated for the second time after being heated by the preheater.
进一步的,第二次加热热媒为生蒸汽,加热方式为板式换热器加热。Further, the heating medium for the second heating is raw steam, and the heating method is heating by a plate heat exchanger.
进一步的,含有结晶盐物料经过稠厚器沉降后体积固液比≥30%。Further, the volume solid-liquid ratio of the material containing crystalline salt is ≥30% after being settled by the thickener.
进一步的,经过加压加温后蒸汽先进入强制循环蒸发器后进入降膜蒸发器加热物料。Further, after being pressurized and heated, the steam first enters the forced circulation evaporator and then enters the falling film evaporator to heat the material.
本发明为了适应垃圾飞灰水洗液成分复杂且含盐浓度高特点,将蒸发浓缩和蒸发结晶分为两个相对独立的单元,利用MVR蒸发技术,热能由压缩机系统提供和维持平衡;蒸发浓缩单元包括预热器、降膜蒸发器和降膜分离器,通过对垃圾飞灰水洗液预热、反复蒸发,物料得到了浓缩但未达到饱和状态;蒸发结晶单元包括强制循环分离器、强制循环蒸发器,蒸发浓缩物料经过此单元进一步蒸发后,物料达到了饱和或过饱和状态,结晶盐开始析出;本发明后续设置稠厚器和离心机,首先将含有结晶盐物料进一步沉降浓缩,达到离心分离要求后,通过离心机有效分离后,结晶盐最终排到系统之外。In order to adapt to the characteristics of complex components and high salt concentration of garbage fly ash washing liquid, the present invention divides evaporation concentration and evaporation crystallization into two relatively independent units, and utilizes MVR evaporation technology, and the heat energy is provided by the compressor system and maintained in balance; evaporation concentration The unit includes a preheater, a falling film evaporator and a falling film separator. Through preheating and repeated evaporation of the garbage fly ash washing liquid, the material is concentrated but not saturated; the evaporation crystallization unit includes a forced circulation separator, a forced circulation Evaporator, after the evaporative and concentrated material is further evaporated through this unit, the material reaches a saturated or supersaturated state, and the crystalline salt begins to precipitate; in the present invention, a thickener and a centrifuge are set up to further settle and concentrate the material containing the crystalline salt to achieve centrifugation. After separation requirements, after being effectively separated by a centrifuge, the crystallized salts are finally discharged out of the system.
本发明的有益效果是:(1)采用降膜蒸发器和强制循环蒸发器对物料进行蒸发浓缩,适应了垃圾飞灰水洗液料性,并且具有节能效果更为显著的特点;(2)垃圾飞灰水洗液经过预热、蒸发和深度蒸发步骤,蒸发能力大,且系统运行非常稳定;(3)采用稠厚器和离心机使结晶盐得到了分离,分离效率高且出盐顺畅;(4)对垃圾飞灰水洗液含盐浓度波动大特点具有很好的适应性,含盐浓度适应范围可为0-10%;(5)本发明创新性强,具有很好的操作灵活性、设备工作弹性和长期稳定性The beneficial effects of the present invention are: (1) adopt falling film evaporator and forced circulation evaporator to evaporate and concentrate the material, adapt to the material property of waste fly ash washing liquid, and have the characteristics of more remarkable energy saving effect; (2) The fly ash washing liquid has gone through the steps of preheating, evaporation and deep evaporation, and the evaporation capacity is large, and the system operation is very stable; (3) The thickener and centrifuge are used to separate the crystallized salt, with high separation efficiency and smooth salt discharge; ( 4) It has good adaptability to the characteristics of large fluctuations in the salt concentration of the garbage fly ash washing liquid, and the adaptable range of the salt concentration can be 0-10%; (5) The invention is highly innovative and has good operational flexibility, Equipment working flexibility and long-term stability
附图说明Description of drawings
图1为垃圾飞灰水洗液蒸发脱盐系统工艺流程框图。Figure 1 is a block diagram of the process flow of the waste fly ash water washing liquid evaporation desalination system.
图中:1-预热器;2-降膜蒸发器;3-降膜分离器;4-强制循环分离器;5-强制循环蒸发器;6-稠厚器;7-离心机;8-母液罐;9-压缩机系统;10-冷凝水罐。In the figure: 1-preheater; 2-falling film evaporator; 3-falling film separator; 4-forced circulation separator; 5-forced circulation evaporator; 6-thickener; 7-centrifuge; 8- Mother liquor tank; 9-compressor system; 10-condensate water tank.
具体实施方式Detailed ways
本发明的技术方案之一为一种垃圾飞灰水洗液蒸发脱盐系统,下面结合附图对其作详细说明。One of the technical proposals of the present invention is an evaporative desalination system for garbage fly ash washing liquid, which will be described in detail below with reference to the accompanying drawings.
如图1所示,一种垃圾飞灰水洗液蒸发脱盐系统,包括预热器1、降膜蒸发器2、降膜分离器3、强制循环分离器4、强制循环蒸发器5、稠厚器6、离心机7、母液罐8、压缩机系统9和冷凝水罐10.As shown in Figure 1, an evaporation and desalination system for garbage fly ash washing liquid includes a preheater 1, a falling film evaporator 2, a falling film separator 3, a forced circulation separator 4, a forced circulation evaporator 5, and a thickener 6. Centrifuge 7, mother liquid tank 8, compressor system 9 and condensed water tank 10.
上述系统中,预热器1冷媒进口前安装进料泵,通过进料泵将经过除钙等处理后的垃圾飞灰水洗液打入与冷凝水换热,预热器1冷媒出口与降膜蒸发器2进料口相连,降膜蒸发器2上部设有布液盘,通过布液盘的分散作用,垃圾飞灰水洗液均匀进入降膜蒸发器2的管程列管中,从上而下缓缓流下中与降膜蒸发器2的壳程蒸汽换热,达到了沸点形成了蒸发状态。In the above system, a feed pump is installed before the refrigerant inlet of the preheater 1, and the garbage fly ash washing liquid after decalcification and other treatments is pumped into the condensed water through the feed pump to exchange heat with the condensed water. The feed port of the evaporator 2 is connected, and the upper part of the falling film evaporator 2 is equipped with a liquid distribution plate. Through the dispersing effect of the liquid distribution plate, the garbage fly ash washing liquid enters the tube-side tubes of the falling film evaporator 2 evenly, from top to bottom Slowly flowing downwards, the heat exchange with the shell-side steam of the falling film evaporator 2 reaches the boiling point and forms an evaporation state.
降膜蒸发器2出料口与降膜分离器3进口连接,经过降膜蒸发器2蒸发后物料进入降膜分离器3进行气液分离,降膜分离器3设有两个液体出口,其一液体出口通过循环泵与降膜蒸发器2进料口连接,使物料在降膜蒸发器2中反复蒸发,另一液体出口通过转料泵与强制循环分离器4一液体进口连接,从而使经过气液分离后的高浓液体转向结晶单元。The outlet of the falling film evaporator 2 is connected to the inlet of the falling film separator 3, and after being evaporated by the falling film evaporator 2, the material enters the falling film separator 3 for gas-liquid separation. The falling film separator 3 is provided with two liquid outlets. One liquid outlet is connected to the feed port of the falling film evaporator 2 through a circulation pump, so that the material is repeatedly evaporated in the falling film evaporator 2, and the other liquid outlet is connected to the liquid inlet of the forced circulation separator 4 through a transfer pump, so that the After gas-liquid separation, the high-concentration liquid turns to the crystallization unit.
强制循环分离器4设置有三个液体进口和两个液体出口,其中一个液体进口与强制循环蒸发器5出料口相连,其中一个液体出口通过强制循环泵与强制循环蒸发器5进料口相连,另一个液体出口通过出料泵与稠厚器6进口相连,第二个液体进口通过母液泵与母液罐8出口连接;强制循环分离器4是结晶单元非常重要的设备,垃圾飞灰水洗液浓缩液通过在强制循环蒸发器5中进一步蒸发,在强制循环分离器4达到饱和或过饱和,从而使结晶盐析出。The forced circulation separator 4 is provided with three liquid inlets and two liquid outlets, wherein one of the liquid inlets is connected with the forced circulation evaporator 5 outlets, and one of the liquid outlets is connected with the forced circulation evaporator 5 feed ports through the forced circulation pump, The other liquid outlet is connected to the thickener 6 inlet through the discharge pump, and the second liquid inlet is connected to the mother liquor tank 8 outlet through the mother liquor pump; the forced circulation separator 4 is a very important equipment of the crystallization unit, and the waste fly ash washing liquid is concentrated The liquid is further evaporated in the forced circulation evaporator 5, and reaches saturation or supersaturation in the forced circulation separator 4, so that the crystalline salt is precipitated.
稠厚器6溢流口与母液罐8一进口连接,稠厚器6下料口与离心机7进料口连接;离心机7母液出口与母液罐8另一进口连接;含有结晶盐的物料在稠厚器6沉降后,稠厚器6上清液进入母液罐8,底部浓液体积固液比达到30%后,进入到两级活塞推料离心机或卧螺离心机中进行固液分离,从而得到了结晶盐,而离心分离母液进入母液罐8与稠厚器6上清液一起返回至强制循环分离器4进行再次蒸发。The overflow port of the thickener 6 is connected to the inlet of the mother liquor tank 8, and the feed port of the thickener 6 is connected to the feed inlet of the centrifuge 7; the mother liquor outlet of the centrifuge 7 is connected to the other inlet of the mother liquor tank 8; the material containing crystallized salt After the thickener 6 settles, the supernatant of the thickener 6 enters the mother liquor tank 8, and after the solid-liquid ratio of the concentrated liquid at the bottom reaches 30%, it enters a two-stage piston pusher centrifuge or a decanter centrifuge for solid-liquid Separation, thereby obtained crystalline salt, and centrifugal separation mother liquor enters mother liquor tank 8 and returns to forced circulation separator 4 together with thickener 6 supernatant and evaporates again.
降膜分离器3与强制循环分离器4蒸汽出口经管道汇合后与压缩机系统9蒸汽进口相连,通过压缩机系统9加压提温作用,蒸汽温度得以升高,满足蒸发换热要求;压缩机系统9蒸汽出口与强制循环蒸发器5蒸汽进口连接;强制循环蒸发器5蒸汽出口与降膜蒸发器2蒸汽进口连接,强制循环蒸发器5冷凝水出口与和冷凝水罐10一进口连接,降膜蒸发器2冷凝水出口与冷凝水罐10另一进口连接,即强制循环蒸发器5和降膜蒸发器2换热后的高温冷凝水都进入冷凝水罐10;冷凝水罐10出口通过冷凝水泵与预热器1热媒进口连接,通过预热器1换热,冷凝水温度降至40℃左右。The steam outlet of the falling film separator 3 and the forced circulation separator 4 are connected to the steam inlet of the compressor system 9 after being merged through the pipeline, and the temperature of the steam is raised through the pressurization and temperature raising of the compressor system 9 to meet the requirements of evaporation and heat exchange; The steam outlet of the machine system 9 is connected to the steam inlet of the forced circulation evaporator 5; the steam outlet of the forced circulation evaporator 5 is connected to the steam inlet of the falling film evaporator 2, and the condensed water outlet of the forced circulation evaporator 5 is connected to the inlet of the condensed water tank 10, The condensed water outlet of the falling film evaporator 2 is connected to the other inlet of the condensed water tank 10, that is, the high-temperature condensed water after the heat exchange between the forced circulation evaporator 5 and the falling film evaporator 2 enters the condensed water tank 10; the outlet of the condensed water tank 10 passes through The condensed water pump is connected to the heat medium inlet of the preheater 1, and the heat exchanged through the preheater 1 reduces the temperature of the condensed water to about 40°C.
所述预热器1为板式换热器,具有换热速度快、换热效率高的特点。The preheater 1 is a plate heat exchanger, which has the characteristics of fast heat exchange speed and high heat exchange efficiency.
所述强制循环分离器4为正循环切向进料蒸发器,有利于结晶盐析出并增大,满足后续离心脱盐要求。The forced circulation separator 4 is a positive circulation tangentially fed evaporator, which is conducive to the precipitation and increase of crystalline salts, and meets the requirements of subsequent centrifugal desalination.
本发明的另一技术方案是一种垃圾飞灰水洗液蒸发脱盐方法,下面通过实例对其作详细说明。Another technical solution of the present invention is a method for evaporative desalination of rubbish fly ash washing liquid, which will be described in detail through examples below.
实例1Example 1
一种垃圾飞灰水洗液蒸发脱盐方法,包括如下步骤:A method for evaporating and desalting garbage fly ash water washing liquid, comprising the steps of:
1)开启进料泵,将预处理后的含盐浓度8%的垃圾飞灰水洗液打入预热器进行加热,加热热媒为换热后的冷凝水,控制加热后物料温度≥95°;1) Turn on the feed pump, inject the pretreated garbage fly ash washing solution with a salt concentration of 8% into the preheater for heating, the heating medium is condensed water after heat exchange, and control the material temperature after heating to ≥95° ;
2)预热后物料进入降膜蒸发器进行蒸发浓缩,控制降膜蒸发器内的蒸发温度为103-104℃;2) After preheating, the material enters the falling film evaporator for evaporation and concentration, and the evaporation temperature in the falling film evaporator is controlled to be 103-104°C;
3)蒸发浓缩后含盐浓度20-27%的物料进入降膜分离器进行气液分离,分离后蒸汽进入压缩机系统,分离后一部分液体通过循环泵返回降膜蒸发器继续蒸发,另一部分液体由转料泵打入强制循环分离器;3) After evaporation and concentration, the material with a salt concentration of 20-27% enters the falling film separator for gas-liquid separation. After separation, the steam enters the compressor system. After separation, part of the liquid returns to the falling film evaporator through the circulating pump to continue evaporation, and the other part It is pumped into the forced circulation separator by the material transfer pump;
4)强制循环分离器内物料通过外接的强制循环蒸发器进行深度蒸发浓缩,控制强制循环分离器内液相温度为108-109℃;4) The material in the forced circulation separator is subjected to deep evaporation and concentration through an external forced circulation evaporator, and the temperature of the liquid phase in the forced circulation separator is controlled to be 108-109°C;
5)强制循环分离器内物料达到饱和或过饱和后迅速气液分离,分离后蒸汽进入压缩机系统,分离后液体有小颗粒结晶盐析出,结晶盐下落至强制循环分离器底部后由出料泵送入稠厚器;5) After the material in the forced circulation separator reaches saturation or supersaturation, the gas-liquid separation is rapid. After separation, the steam enters the compressor system. After separation, the liquid has small particles of crystallized salt. pumped into the thickener;
6)含有结晶盐物料在稠厚器内沉降后,控制浓缩物料体积固液比≥30%,上清液溢流至母液罐,浓缩物料进入离心机分离后得到结晶盐,而离心母液进入母液罐,母液罐物料由母液泵打入强制循环分离器内继续蒸发浓缩;6) After the material containing crystalline salt settles in the thickener, control the volume solid-liquid ratio of the concentrated material to ≥ 30%, the supernatant overflows to the mother liquor tank, and the concentrated material enters the centrifuge for separation to obtain crystallized salt, and the centrifuged mother liquor enters the mother liquor Tank, the mother liquor tank material is pumped into the forced circulation separator by the mother liquor pump to continue to evaporate and concentrate;
7)进入压缩机系统的蒸汽经过加压升温至116℃后,先进入强制循环蒸发器后进入降膜蒸发器加热物料,经过换热的冷凝水进入冷凝水罐后由冷凝水泵送至预热器对垃圾飞灰水洗液进行加热。7) After the steam entering the compressor system is pressurized and heated to 116°C, it first enters the forced circulation evaporator and then enters the falling film evaporator to heat the material. The condensed water after heat exchange enters the condensed water tank and is pumped to the preheating The device heats the garbage fly ash washing liquid.
实例2Example 2
一种垃圾飞灰水洗液蒸发脱盐方法,包括如下步骤:A method for evaporating and desalting garbage fly ash water washing liquid, comprising the steps of:
1)开启进料泵,将预处理后的含盐浓度10%的垃圾飞灰水洗液打入预热器进行加热,加热热媒为换热后的冷凝水,控制加热后物料温度≥95°;1) Turn on the feed pump, inject the pretreated garbage fly ash washing solution with a salt concentration of 10% into the preheater for heating, the heating medium is condensed water after heat exchange, and control the material temperature after heating to ≥95° ;
2)预热后物料进入降膜蒸发器进行蒸发浓缩,控制降膜蒸发器内的蒸发温度为105-106℃;2) After preheating, the material enters the falling film evaporator for evaporation and concentration, and the evaporation temperature in the falling film evaporator is controlled at 105-106°C;
3)蒸发浓缩后含盐浓度20-27%的物料进入降膜分离器进行气液分离,分离后蒸汽进入压缩机系统,分离后一部分液体通过循环泵返回降膜蒸发器继续蒸发,另一部分液体由转料泵打入强制循环分离器;3) After evaporation and concentration, the material with a salt concentration of 20-27% enters the falling film separator for gas-liquid separation. After separation, the steam enters the compressor system. After separation, part of the liquid returns to the falling film evaporator through the circulating pump to continue evaporation, and the other part It is pumped into the forced circulation separator by the material transfer pump;
4)强制循环分离器内物料通过外接的强制循环蒸发器进行深度蒸发浓缩,控制强制循环分离器内液相温度为110-111℃;4) The material in the forced circulation separator is subjected to deep evaporation and concentration through an external forced circulation evaporator, and the temperature of the liquid phase in the forced circulation separator is controlled to be 110-111°C;
5)强制循环分离器内物料达到饱和或过饱和后迅速气液分离,分离后蒸汽进入压缩机系统,分离后液体有小颗粒结晶盐析出,结晶盐下落至强制循环分离器底部后由出料泵送入稠厚器;5) After the material in the forced circulation separator reaches saturation or supersaturation, the gas-liquid separation is rapid. After separation, the steam enters the compressor system. After separation, the liquid has small particles of crystallized salt. pumped into the thickener;
6)含有结晶盐物料在稠厚器内沉降后,控制浓缩物料体积固液比≥40%,上清液溢流至母液罐,浓缩物料进入离心机分离后得到结晶盐,而离心母液进入母液罐,母液罐物料由母液泵打入强制循环分离器内继续蒸发浓缩;6) After the material containing crystalline salt settles in the thickener, control the volume solid-liquid ratio of the concentrated material to ≥ 40%, the supernatant overflows to the mother liquor tank, and the concentrated material enters the centrifuge for separation to obtain crystallized salt, and the centrifuged mother liquor enters the mother liquor Tank, the mother liquor tank material is pumped into the forced circulation separator by the mother liquor pump to continue to evaporate and concentrate;
7)进入压缩机系统的蒸汽经过加压升温至117℃后,先进入强制循环蒸发器后进入降膜蒸发器加热物料,经过换热的冷凝水进入冷凝水罐后由冷凝水泵送至预热器对垃圾飞灰水洗液进行加热。7) After the steam entering the compressor system is pressurized and heated to 117°C, it first enters the forced circulation evaporator and then enters the falling film evaporator to heat the material. The condensed water after heat exchange enters the condensed water tank and is pumped to the preheating The device heats the garbage fly ash washing liquid.
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Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN201082325Y (en) * | 2008-01-09 | 2008-07-09 | 光大环保工程技术(深圳)有限公司 | Garbage flying ash innocent treatment system |
US20100172819A1 (en) * | 2009-01-06 | 2010-07-08 | Paul Steven Wallace | Methods and systems for zero discharge water treatment |
CN101851041A (en) * | 2010-04-27 | 2010-10-06 | 中国海诚工程科技股份有限公司 | Method and device for realizing zero release in desulfuration wastewater deepening treatment |
CN202594905U (en) * | 2012-02-23 | 2012-12-12 | 北京浦仁美华节能环保科技有限公司 | MVR (mechanical vapor recompression) efficient and energy-saving evaporating system |
CN204779210U (en) * | 2015-07-18 | 2015-11-18 | 北京建筑材料科学研究总院有限公司 | Rubbish flying dust washing liquid evaporation desalination system |
-
2015
- 2015-07-18 CN CN201510430270.0A patent/CN105016555A/en active Pending
Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN201082325Y (en) * | 2008-01-09 | 2008-07-09 | 光大环保工程技术(深圳)有限公司 | Garbage flying ash innocent treatment system |
US20100172819A1 (en) * | 2009-01-06 | 2010-07-08 | Paul Steven Wallace | Methods and systems for zero discharge water treatment |
CN101851041A (en) * | 2010-04-27 | 2010-10-06 | 中国海诚工程科技股份有限公司 | Method and device for realizing zero release in desulfuration wastewater deepening treatment |
CN202594905U (en) * | 2012-02-23 | 2012-12-12 | 北京浦仁美华节能环保科技有限公司 | MVR (mechanical vapor recompression) efficient and energy-saving evaporating system |
CN204779210U (en) * | 2015-07-18 | 2015-11-18 | 北京建筑材料科学研究总院有限公司 | Rubbish flying dust washing liquid evaporation desalination system |
Cited By (30)
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CN106007137A (en) * | 2016-06-20 | 2016-10-12 | 常州中源工程技术有限公司 | Electroplating wastewater treatment device and method |
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